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Biodegradation of RDX and HMX by a methanogenic enrichment culture

机译:产甲烷富集培养对RDX和HMX的生物降解

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The biotransformation of RDX and HMX by a methanogenic enrichment culture was studied. The enrichment culture only degraded RDX when ethanol was included as an electron donor. Methane production, however, was only observed after RDX had been depleted. The addition of BESA inhibited methane production, but not ethanol fermentation nor RDX degradation. The addition of H_2 gas supported RDX degradation. HMX was also degraded, but the degradation rate (0.12 #mu#M day ~(-1)) was nearly 10-fold less than observed for RDX (1.6#mu#M day~(-1)). HMX degradation slowed when ethnaol was depleted, but resumed after reamending the bottles with ethanol. The total number of anaerobes in the enrichment culture ranged from 1.5x10~5 to 1.6 x 10~6 ml~(-1). Ethanol-fermenting syntrophs ranged from 1.5x10~4 to 1.6 x10~5 ml-1; H_2-utilizing methanogens ranged from 7.0x10~1 ml~(-1); and H_2-utilizing acetogens ranged from 3.8x10~3 to 2.4 x 10~4 ml~(-1). These findings indicate ethanol may serve as a source of H_2 for the RDX and HMX degrading bacteria. The presence of acetogens and a lack of CH_4 production during ethanol degradation may indicate their involvement in the biodegradation of nitramine explosives.
机译:研究了产甲烷富集培养对RDX和HMX的生物转化作用。当包括乙醇作为电子供体时,富集培养仅降解RDX。但是,只有在RDX耗尽后才能观察到甲烷的产生。 BESA的添加抑制了甲烷的产生,但没有抑制乙醇发酵,也没有抑制RDX降解。加入H_2气体有助于RDX降解。 HMX也被降解,但是降解速率(0.12#mu#M天〜(-1))比RDX(1.6#mu#M天〜(-1))低了近十倍。乙醇耗尽后,HMX的降解速度减慢,但在用乙醇重新填充瓶子后又恢复了HMX的降解。富集培养中厌氧菌的总数为1.5x10〜5至1.6 x 10〜6 ml〜(-1)。乙醇发酵合成物的范围从1.5x10〜4到1.6x10〜5 ml-1。利用H_2的产甲烷菌的范围为7.0x10〜1 ml〜(-1);利用H_2的乙酸原为3.8×10〜3至2.4×10〜4ml〜(-1)。这些发现表明乙醇可作为RDX和HMX降解细菌的H_2来源。在乙醇降解过程中,存在乙酸原和缺乏CH_4的产生可能表明它们参与了硝胺炸药的生物降解。

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